Registration Dossier
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Diss Factsheets
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EC number: 701-197-2 | CAS number: -
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data

Biodegradation in soil
Administrative data
- Endpoint:
- biodegradation in soil: simulation testing
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- data waiving: supporting information
Reference
- Endpoint:
- partition coefficient
- Type of information:
- (Q)SAR
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Scientifically accepted calculation method.
- Justification for type of information:
- QSAR prediction
- Principles of method if other than guideline:
- KOWWIN v1.67 uses the chemical structure of a compound to predict the logarithmic octanol-water partition coefficient (logPow), which is calculated by determining LogPow contributions from individual molecular fragments and then summing up these contributions.
- GLP compliance:
- no
- Remarks:
- Not applicable.
- Type of method:
- other: QSAR prediction
- Partition coefficient type:
- octanol-water
- Type:
- log Pow
- Partition coefficient:
- -1.78
- Remarks on result:
- other: Main component with clorine
- Type:
- log Pow
- Partition coefficient:
- -1.94
- Remarks on result:
- other: Main component without chlorine
- Details on results:
- The single fragments were detected as: aliphatic carbons (-CH2 (8 times) and –CH (4 times)) with coefficients of 0.49 and 0.36, respectively. A hydroxy aliphatic attach (-OH) with a coefficient of -1.41 and 5 oxygen as aliphatic attachments (-O-) with coefficients of -1.25, each. The main component containing chlorine possesses furthermore a single coefficient of 0.31 for the –CL fragment.
- Conclusions:
- The study report describes a scientifically accepted calculation method for determination of the partition coefficient using the US-EPA software KOWWIN v1.67. No GLP criteria are applicable for the usage of this tool and the QSAR estimation is easily repeatable.
- Executive summary:
The partition coefficient of the test substance was determined by the computer program KOWWIN v1.67 (EPIWIN software) by US-EPA (Chemservice S.A., 2011; prediction was performed by the data owner). This program uses the chemical structure of a compound to predict the logarithmic octanol-water partition coefficient (logPow). Structures are used in their SMILES notation. LogPow is calculated by determining LogPow contributions from individual molecular fragments and then summing up these contributions. The single fragments were detected as: aliphatic carbons (-CH2 (8 times) and –CH (4 times)) with coefficients of 0.49 and 0.36, respectively. A hydroxy aliphatic attach (-OH) with a coefficient of -1.41 and 5 oxygen as aliphatic attachments (-O-) with coefficients of -1.25, each. The main component containing chlorine possesses furthermore a single coefficient of 0.31 for the –CL fragment. As overall result, the partition coefficient of the substance was calculated to be -1.78 with and -1.94 without chlorine.
- Reason / purpose for cross-reference:
- data waiving: supporting information
Reference
- Endpoint:
- adsorption / desorption
- Remarks:
- adsorption
- Type of information:
- (Q)SAR
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Scientifically accepted calculation method
- Justification for type of information:
- QSAR prediction
- Principles of method if other than guideline:
- KOCWIN program (v4.10): scientifically accepted calculation method for soil adsorption estimation of organic chemicals. Two different models are used for this estimation: the Sabljic Molecular Connectivity Index (MCI) method as well as the so-called traditional method, which is based on the LogPow.
- GLP compliance:
- no
- Remarks:
- not applicable
- Type of method:
- other: QSAR estimation
- Media:
- soil
- Analytical monitoring:
- not required
- Computational methods:
- Using the computer tool KOCWIN v2.00 by US-EPA (EPIWIN) the organic-normalized sorption coefficient for soil (soil adsorption, Koc) can be estimated. The following two different models are used: Salbjic molecular connectivity method (MCI) and the traditional method, which is based on the logPow value of the substance. In general, the MCI method is taken more seriously into account, due to the fact that it includes improved correction factors.
- Phase system:
- other: Koc
- Type:
- other: Koc
- Value:
- 0.203 L/kg
- Remarks on result:
- other: LogPow-based estimate (traditional method)
- Phase system:
- other: Koc
- Type:
- other: Koc
- Value:
- 10 L/kg
- Remarks on result:
- other: MCI method, includes improved correction factors - most relevant
- Validity criteria fulfilled:
- yes
- Remarks:
- scientifically accepted calculation method
- Conclusions:
- The Koc of the substance 1,2,3-propanetriol, glycidyl ethers was calculated to be 10 L/kg using the MCI method of KOCWIN program (v4.10), whereby the traditional method reveals a value of 0.2034 L/kg. In general, the MCI method is taken more seriously into account, due to the fact that it includes improved correction factors.
- Executive summary:
The prediction for soil adsorption property of the substance 1,2,3-propanetriol, glycidyl ethers was determined by the computer program KOCWIN v2.00 (EPIWIN software) by US-EPA (Chemservice GmbH, 2011). The program estimates the organic-normalized sorption coefficient for soil, which is designated as Koc. The following two models are used: the Salbjic molecular connectivity (MCI) method as well as the traditional method which is based on the logPow value of the substance. The MCI method is taken more seriously into account, due to the fact that is includes improved correction factors, resulting in a Koc value of 10 L/kg. The traditional method gives a value of 0.2034 L/kg.
Data source
Materials and methods
Results and discussion
Applicant's summary and conclusion
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